IL112562A - Water treatment method and apparatus - Google Patents

Water treatment method and apparatus

Info

Publication number
IL112562A
IL112562A IL112562A IL11256295A IL112562A IL 112562 A IL112562 A IL 112562A IL 112562 A IL112562 A IL 112562A IL 11256295 A IL11256295 A IL 11256295A IL 112562 A IL112562 A IL 112562A
Authority
IL
Israel
Prior art keywords
basin
water
diffusor
foam
slurry
Prior art date
Application number
IL112562A
Other versions
IL112562A0 (en
Original Assignee
Puraq As
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Puraq As filed Critical Puraq As
Publication of IL112562A0 publication Critical patent/IL112562A0/en
Publication of IL112562A publication Critical patent/IL112562A/en

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/12Activated sludge processes
    • C02F3/1236Particular type of activated sludge installations
    • C02F3/1257Oxidation ditches
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01KANIMAL HUSBANDRY; CARE OF BIRDS, FISHES, INSECTS; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
    • A01K63/00Receptacles for live fish, e.g. aquaria; Terraria
    • A01K63/04Arrangements for treating water specially adapted to receptacles for live fish
    • A01K63/042Introducing gases into the water, e.g. aerators, air pumps
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/24Treatment of water, waste water, or sewage by flotation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/06Aerobic processes using submerged filters
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/12Activated sludge processes
    • C02F3/20Activated sludge processes using diffusers
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Organic Chemistry (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Microbiology (AREA)
  • Environmental Sciences (AREA)
  • Animal Husbandry (AREA)
  • Marine Sciences & Fisheries (AREA)
  • Physical Water Treatments (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)
  • Water Treatment By Sorption (AREA)
  • Electrical Discharge Machining, Electrochemical Machining, And Combined Machining (AREA)
  • Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
  • Excavating Of Shafts Or Tunnels (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

PCT No. PCT/NO95/00027 Sec. 371 Date Sep. 26, 1996 Sec. 102(e) Date Sep. 26, 1996 PCT Filed Feb. 6, 1995 PCT Pub. No. WO95/21134 PCT Pub. Date Aug. 10, 1995Water to be treated is introduced into a basin having a closed bottom and an outer wall. A stationary diffusor is located at the bottom at a position spaced from the outer wall and produces air bubbles of varying size acting to lift water impurities toward the surface of the water and to circulate the water in the basin as a first stream flowing vertically upwardly from the diffusor, horizontally outwardly toward the outer wall, vertically downwardly toward the bottom and horizontally along the bottom back to the diffusor. A second stream is caused to circulate circumferentially in the basin. The first and second circulating streams cooperate to cause foam and slurry formed on the surface to concentrate in an outer peripheral flow path from which the foam and slurry are removed.

Description

WATER TREATMENT METHOD AND APPARATUS The invention relates to a method and apparatus for treating water. More specifically it is a further develop-ment of the method and apparatus described in EP patent publication No. 0 448 597.
As explained in the latter publication the water treatment takes place mainly by flotation and physical adsorption based on air bubbles of varying sizes produced from a diffusor at the bottom of a water basin. Thus, the flotation process is carried out by means of air bubbles of a size ranging from about 0,03 mm up to about 0,12 mm attaching to particles thus increasing their boyancy. the particles as a consequence are forming a slurry at the surface. The adsorption process occurs via air bubbles of a size about 0,8 mm combining with colloidal or dissolved polarized substances and forming therewith a voluminous bubble foam at the water surface.
According to the above patent the diffusor is located in a chamber which is partly separated from the remaining part of the basin by a partition wall and has a substantially smaller volume than that of the latter part. The adsorption process then takes place substantially within this chamber while the flotation process takes place sub-stantially within the basin itself, and the water, owing to the pumping effect from the diffusor bubbles, circulates up through the chamber and out into the basin at the opposite side of the partition wall. The bubble foam is continuously removed as it forms at the water surface in the chamber, while the slurry that is formed way out in the basin is removed at the rim of the basin opposite the chamber. At either place the removal is carried out by allowing the foam and slurry respectively to flow over a weir together with a top water layer.
While the technique according to the above EP patent represents a substantial improvement compared to prior water treatment methods, it also suffers from certain defects and disadvantages. Thus, it is a problem to get the bubble foam at the chamber water surface removed sufficiently rapidly by the weir technique that is used. As noted in the patent it is important to have this foam removed before it disintegrates to drop the impurities back into the water. Another disadvantage is the fact that by the above weir technique a relatively large water flow will accompany the foam and slurry out into the basin.
According to the present invention it has now been found that these defects and disadvantages of the process diclosed in the EP patent can be avoided in a particularly simple manner. ' v Thus, surprisingly it has been found that if the wall that partly separates the chamber from the remaining part of the prior basin is removed, then important advantages may be achieved if, in addition to the laterally directed water circulation that takes place in the basin owing to the diffusor pumping effect, also a longitudinally circulating flow is established in the basin water. Practically all of the foam and slurry on the water surface will then gradually gather in a peripheral flow path in the basin and may easily be removed from one or more places therealong. The foam is viscous and the slurry will intermix with the foam and attach to it thus forming a stabile foam-slurry mixt. According to a preferred embodiment of the invention the foam-slurry mixture is effectively removed from the flow path by means of a suction means communicating with a vacuum source.
The method and device according to the invention are defined in the accompanying patent claims.
The fact that the system according to the invention, contrary to that described in the above EP patent No. 0 448 597 does not include any chamber forming partition wall in the water basin results in a reduced residence time of the foam before it is removed. Furthermore the foam is quickly removed from the turbulent zone above the air diffusors where the foam tends to disintegrate. This results in a lower resuspension of impurities, leading to an enhanced cleaning effect. Additionally, removal of the chamber partition wall allows the foam from the adsorption process to be directed together with the floating slurry from the flotation process interacting with the foam to form a stabile mixture that can be diverted by the flow to a central region in which it can be effectively removed by means of vacuum technique. Furthermore, the vacuum technique will disintegrate the foam and further mix it with the slurry to form a homogenous sludge which allows the suspended matter to be separated from the water phase in an effective manner, i.e. by simple sedimentation, such that the water content of the sludge may be reduced by about 2 orders. This results in a large cost reduction in sludge treatment, which in the earlier patent represented a considerable part of the total costs of the treatment plant.
The invention will be described more fully below with reference to the drawing in which: Fig. 1 is a plan view of a plant based on the method and device according to the invention, Fig. 2 is an enlarged cross sectional view taken on line II-II in fig. 1, Fig. 3 is a cross sectional view taken on line III- III, Fig. 4 is a vector diagram showing relative flow rates at different depths of the cross section shown in fig. 2, Fig. 5 is a further enlarged cross sectional view taken on line IV-IV in fig. 1, Fig. 6 is a plan view of an other embodiment of the basin with the device according to the invention.
The plant shown in the drawing is primarily, but not exclusively, built for fish fattening. It comprises a water basin 2 which, in the example shown in fig. 1, has a longitudinal rectangular peripheral wall including side walls 4 and end walls 6. The basin may have a base surface of about 10 x 50 m, for example, and built for a normal water depth of about 3 m.
Centrally located between the side walls 4 the basin of the embodiment shown in fig. 1 has a longitudinal inner wall 8 serving to form a circumferential channel 10 in the basin 2. Preferably the inner wall extends along the major part of the basin and terminates at a distance from one end wall 6 thereof, such that the water may pass without excessive pressure drop. At the other end there is a flow generator 16, from reasons to be explained below. The flow generator 16 may, for example, be in the form of one or more propellers 12 mounted in a respective opening 13 in inner wall 8 as shown in fig. 3.
At the bottom of the basin, on either side of the inner wall 8 adjacent thereto and parallel to the longitudinal axis of the basin there is a longitudinal tubular air diffusor 14 of the type described in EP patent No. 0 448 597, i.e. perforated with apertures capable of producing air bubbles in the range of about 0,03 mm to about 1 mm, the larger bubbles acting by physical adsorption to form a contaminated foam on the water surface substantially directly above the air diffusor 14, and the remaining smaller bubbles acting together with the particulates acting to form a flotation slurry containing particulate impurities at the water surface 15 in the basin, as described in detail in the above EP patent publication No. 0 448 597.
Upstrea s of the flow generator 16 and adjacent thereto, such as at the nearest basin corner as shown in fig. 1, there is a foam and slurry removing means 18 to be explained and described more fully below.
As in the plant according to the above EP patent, in operation of the above described plant the air bubbles from the longitudinal diffusors 14 will also act as a flow generator causing a circulation of the basin water laterally of the longitudinal axis of the diffusors 14, i.e. in the lateral direction of the basin. Water is dragged with the rising air bubbles to create a rising flow along the inner wall 8, outwards toward the side walls 4 at the surface 15, down along the side walls and back along the bottom 19 as indicated with arrows A in the left part of the sectional view in fig. 2. Also, in order to better visualize the flow conditions in the basin caused by the diffusor flow generator 14 the right hand part of that drawing figure is provided with two vector diagrams, V2 and Vx, indicating the relative flow velocities in different water layers in the vertical and lateral directions respectively of the basin. Here as well as in the following description it is referred to a x,y,z coordinate system in which z and x refer to the depth and lateral or cross directions respectively of the basin, and y to the longitudinal direction thereof i.e. normal to the plane of the drawing figure 2. As appearing from the diagrams the relative flow velocities in the channel 10, both in the z and x directions, decrease from a maximum near the opposite walls 4, 8 and bottom 19 - water surface 15 respectively, to about zero along its central axis.
At the same time the flow generator 16 in the channel 10 will cause the water in the basin to circulate in the circumferential direction of the basin around the channel 10, as indicated with arrows B in fig. 1, in which a further vector diagram Vy is drawn, indicating that the flow velcoity in the longitudinal direction of the channel caused by the flow generator 16 is substantially constant across the channel cross section, at least in the water layer adjacent surface 16.
Thus, the two above described circulation streams A, B, as caused by the air diffusors 14 and propellers 12 respectively, will create flow components in the x-y directions in different depths (termed "level" a - f in fig. 2), as indicated in the vector diagrams in fig. 4 in which also the resultant ra - rf of the respective flow components are indicated.
The polluted foam and slurry which, owing to the diffusor-based flotation and physical adsorption processes, are formed at the surface 15 of the water in the basin 2, will interact and form a stabile mixture termed foamslurry as it follows the surface water streams according to the resultant ra of the above described lateral and longitudinal flow components x, y respectively. In fig. 1 this is visualized by indicating the path of a pollution particle entrained with the foamslurry, from the point P at which it appears on the surface above the diffusor 14. As schematically indicated it will float obliquely toward the side wall 4 of the basin in accordance with ra and then follow a peripheral or circumferential flow path S around the basin. The same will happen with practically any pollution particle in the foamslurry at the surface, all of which relatively rapidly concentrates in the peripheral flow path S along the edge of the basin from which it may easily be removed by means of the foamslurry removal means 18.
In a preferred embodiment of the plant according to the invention the foamslurry remover 18 comprises a vacuum means, e.g. in the form of a mouth piece 20. As shown in detail in fig. 5 the suction opening 22 of the mouth piece 20 is located at the level of the water surface 15 and may advantageously be surrounded by a screen or skimmer 24 acting to guide the foamslurry toward the suction opening 22. The mouth piece 20 communicates via a pipeline 26 and a vacuum chamber 28 (fig. 1) with a vacuum source 30, such as a fan. The vacuum chamber 28 and source 30 may suitably be positioned in an adjacent room 32 near the suction mouth piece. In operation, the foamslurry and a relatively very small fraction of the surface water are drawn through the mouth piece and into the pipeline were it disintegrate into a thin sludge that enters the vacuum chamber 28 where it can be transferred to an adjacent dewatering vessel 34 in which the sludge is dewatered by any convenient manner.
The water part can be diverted back to the basin 2 as indicated with the arrow C, via a weir 36 schematically indica-ted in fig. 1, or it can be diverted to an effluent pipeline.
Any refilling of water into the basin may advantage- ously take place in the area where the water from the weir 36 enters. This also applies in case the plant is to be used for other purposes than the fattening of fish or the like, such as for treating waste water, sewage or other polluted water, in which case treated water would tapped off centrally in the water column in the area between the mouth piece 20 and flow generator 16, in an amount equalling that of the inflowing polluted water. If, in addition to the flotation and physical adoption processes, it is desireable or necessary to have the basin water filtered through a biofilter, such as of the type noted in NO patent No. 172 487, this may advantageously take place in a conventional manner by permitting the basin water to flow through an external circulation circuit (not shown) in which the biofilter is incorporated.
While the rectangular longitudinal shape of the water basin with the water treatment device according to the invention as shown in fig. 1 has been found to be the most convenient one, particularly in connection with use as a fish fattening plant, it is within the scope of the invention to give the basin any other shape that would be convenient for the intended use, such as circular or oval.
An example of a such circular basin 2' is shown in fig. 6. Here the diffusor means 14' is arranged without any inner wall centrally at the bottom of the basin. The flow generator 16', in the form of a propeller or similar, is disposed near the basin peripheral wall 4· and the foamslurry removal means 18' is positioned relatively close to the flow generator upstream thereof. Otherwise the suction system 20, 24, 26, 28, 30 etc is the same as in the previous example. Here, the diffusor 14' will cause a radially outwardly directed flow component at the water surface, with the result that a polluted particle would float from a point P' in the area above the diffusor cur-vingly toward the basin peripheral wall 4' and thence follow a peripheral flow path S' around the basin 2» until it is drawn into the foamslurry removal means 18'.

Claims (8)

P A T E N T C L A I M S :
1. Water treatment method in which the water to be treated is introduced into a basin (2) and aerated by means of a diffusor means (14) located near the bottom of the basin to produce air bubbles of varying size acting to carry water impurities toward the surface (15) and to circulate the water in the basin as a first stream (A) directed outwards from the diffusor means, and in which polluted foam and slurry formed on the water surface by the effect of the diffusor air bubbles is removed therefrom, c h a r a c t e r i z e d by causing the water to circulate as a second flow (B) circumferentially in the basin (2) , the two circulation streams (A, B) cooperating to concentrate the foam and slurry formed on the water surface in a peripheral flow path (S) , where the foam and slurry are interacting to form a stable compound termed foamslurry and removing the foam and slurry from the basin at one or more places along the peripheral flow path.
2. Method according to claim 1, c h a r a c t e r i z e d by removing the foamslurry from the peripheral flow path by suction.
3. Method according to claims 1 or 2, in which the foamslurry are disintegrated upon transport in pipeline forming a thin sludge which in turn are dewatered, c h a r a c t e r i z e d by returning the water to the main basin via weir from an adjacent dewatering vessel.
4. Water treatment apparatus comprising a basin (2) for the water to be treated, a diffusor means (14) located near the bottom of the basin and designed to produce air bubbles of varying sizes acting to bring water impurities toward the surface and to circulate the water in the basin as a first stream (A) in a direction outward from the diffusor means, and a means (18) for removing polluted foam and slurry formed at the water surface (15) by the effect of the diffusor air bubbles, c h a r a c t e r i z e d by comprising a flow generator (16) located in the basin (2) and adapted to circulate the water therein as a second stream (B) circumferentially in the basin, the two circulation streams (A, B) cooperating to form a peripheral flow path (S) in which the foam and slurry on the water surface (15) concentrate, and by said means (18) for removing the foam and slurry being located at one or more places along the peripheral flow path (S) .
5. Apparatus according to claim 4, in which the basin is of a rectangular shape with side walls (4) and end walls (6) , c h a r a c t e r i z e d by an inner wall (8) centrally between the side walls (4) of the basin, acting to form a circumferential channel (10) in the basin, said flow generator being located in an opening (15) in the inner wall near an end wall (6), and the diffusor means (14) being located along the inner wall (8) .
6. Apparatus according to claim 4, in which the basin (2') has a circular peripheral wall (4'), c h a r a c t e r i z e d by said diffusor means (14') being located centrally at the bottom of the basin, while the flow generator (16') is located at the peripheral wall of the basin.
7. Apparatus according to any one of claims 4 - 6, c h a r a c t e r i z e d by said foamslurry remover (18) being in the form of a suction means (20) communicating with a vacuum source (30).
8. Apparatus according to claims 5 and 6, c h a r a c t e r i z e d by said suction means (20) being surrounded by a skimmer (24) adapted to foamslurry toward the suction means. S. HOROWITZ & CO. AGENT FOR THE APPLICANT
IL112562A 1994-02-07 1995-02-07 Water treatment method and apparatus IL112562A (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
NO940390A NO180744C (en) 1994-02-07 1994-02-07 Method and apparatus for purifying water

Publications (2)

Publication Number Publication Date
IL112562A0 IL112562A0 (en) 1995-05-26
IL112562A true IL112562A (en) 1998-02-08

Family

ID=19896818

Family Applications (1)

Application Number Title Priority Date Filing Date
IL112562A IL112562A (en) 1994-02-07 1995-02-07 Water treatment method and apparatus

Country Status (26)

Country Link
US (1) US5814229A (en)
EP (1) EP0743926B1 (en)
JP (1) JP3274685B2 (en)
KR (1) KR100310673B1 (en)
CN (1) CN1077866C (en)
AT (1) ATE158265T1 (en)
AU (1) AU677898B2 (en)
CA (1) CA2182802A1 (en)
DE (1) DE69500738T2 (en)
DK (1) DK0743926T3 (en)
EG (1) EG22476A (en)
ES (1) ES2106639T3 (en)
FI (1) FI963099A (en)
GR (1) GR3025457T3 (en)
IL (1) IL112562A (en)
IS (1) IS1699B (en)
JO (1) JO1827B1 (en)
MA (1) MA23444A1 (en)
MY (1) MY111818A (en)
NO (2) NO180744C (en)
NZ (1) NZ279921A (en)
PE (1) PE22595A1 (en)
TN (1) TNSN95009A1 (en)
TW (1) TW374754B (en)
WO (1) WO1995021134A1 (en)
ZA (1) ZA95830B (en)

Families Citing this family (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
SE9502459L (en) * 1995-07-06 1996-07-08 Andreas Schelin Device for separating oil from water
US20040149234A1 (en) * 2002-12-04 2004-08-05 Mathur Ashok N. Decentralized oxygen supply system for aquaculture
JP4538479B2 (en) * 2007-09-04 2010-09-08 日本製紙株式会社 Floatator
US9095786B1 (en) * 2011-03-04 2015-08-04 Enviro-Tech Systems, L.L.C. Method and apparatus for separation of fluids within a single vessel
CN103972593A (en) * 2014-05-23 2014-08-06 江苏三环实业股份有限公司 Acid mixing box for lead-acid storage battery formation system
CN105210976A (en) * 2014-06-27 2016-01-06 郭其哲 The treatment facility of high-density breeding cycle water
KR20160002656U (en) 2015-01-21 2016-07-29 이준석 A packing box roll tape cutting machine
JP6602133B2 (en) * 2015-09-25 2019-11-06 グンジ株式会社 Ginger cleaning system for live squid
CN105923756B (en) * 2016-07-10 2019-01-18 赖柱彭 A kind of aeration cell system
JP6445200B2 (en) * 2017-06-02 2018-12-26 株式会社林養魚場 Seafood farming equipment
CN109006648A (en) * 2018-07-28 2018-12-18 福建省水产技术推广总站 Water body is removed contamination system and its application
CN109220971B (en) * 2018-09-30 2021-06-01 祝煜 Oxygenation equipment for aquaculture

Family Cites Families (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB830531A (en) *
US2418950A (en) * 1944-06-12 1947-04-15 Lakeside Engineering Corp Settling tank
GB1058914A (en) * 1965-06-14 1967-02-15 Outokumpu Oy Froth flotation apparatus
GB1442547A (en) * 1974-04-24 1976-07-14 Ishigaki Mech Ind Apparatus for treating waste water
DE3126832C2 (en) * 1981-07-08 1985-03-28 Maschinenfabrik Hellmut Geiger Gmbh & Co Kg, 7500 Karlsruhe Aeration basins for sewage treatment plants with a round or almost square plan
JPS58174289A (en) * 1982-04-07 1983-10-13 Kyoritsu Yuki Kogyo Kenkyusho:Kk Biologically treating device of unit type using fluidized carrier
US4721562A (en) * 1984-04-03 1988-01-26 Feldmuele Aktiengesellschaft Aerating apparatus
DE3417550A1 (en) * 1984-05-11 1985-11-14 Linde Ag, 6200 Wiesbaden METHOD FOR BIOLOGICAL WASTE WATER TREATMENT
DE3643931A1 (en) * 1986-12-22 1988-07-07 Kernforschungsanlage Juelich FUMING / FLOTATION REACTOR
NO885455L (en) * 1988-12-08 1990-06-11 Sunfish Ltd As PROCEDURE AND APPARATUS FOR WATER CLEANING.
JP2790338B2 (en) * 1989-10-16 1998-08-27 石川島播磨重工業株式会社 Flotation device for deinking
DE69102785T2 (en) * 1990-02-09 1994-11-10 Masakatsu Ozawa Device for separation by pressurization and flotation.
US5509535A (en) * 1994-07-12 1996-04-23 Hydrochem Developments Ltd. Flotation apparatus

Also Published As

Publication number Publication date
EP0743926B1 (en) 1997-09-17
AU677898B2 (en) 1997-05-08
JPH09508314A (en) 1997-08-26
MA23444A1 (en) 1995-10-01
JP3274685B2 (en) 2002-04-15
IS4257A (en) 1995-08-08
US5814229A (en) 1998-09-29
EG22476A (en) 2003-02-26
JO1827B1 (en) 1995-07-05
ZA95830B (en) 1996-01-10
FI963099A (en) 1996-08-07
ATE158265T1 (en) 1997-10-15
ES2106639T3 (en) 1997-11-01
IS1699B (en) 1998-10-19
TW374754B (en) 1999-11-21
TNSN95009A1 (en) 1996-02-06
NO180744C (en) 1997-06-11
NO963299L (en) 1996-08-07
AU1719795A (en) 1995-08-21
CN1139913A (en) 1997-01-08
NO963299D0 (en) 1996-08-07
NO313045B1 (en) 2002-08-05
DK0743926T3 (en) 1998-04-14
PE22595A1 (en) 1995-08-07
MY111818A (en) 2001-01-31
IL112562A0 (en) 1995-05-26
EP0743926A1 (en) 1996-11-27
KR100310673B1 (en) 2002-02-28
NO940390D0 (en) 1994-02-07
FI963099A0 (en) 1996-08-06
GR3025457T3 (en) 1998-02-27
DE69500738T2 (en) 1998-04-02
DE69500738D1 (en) 1997-10-23
CN1077866C (en) 2002-01-16
CA2182802A1 (en) 1995-08-10
NO180744B (en) 1997-03-03
WO1995021134A1 (en) 1995-08-10
NO940390L (en) 1995-08-08
NZ279921A (en) 1997-04-24

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